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Importance of Freshwater Mussels for Water Quality in the Tidal Delaware River
Delaware Estuary Science & Environmental Summit
January 29, 2013
Danielle Kreeger, Melanie Mills, Lance Butler, Priscilla Cole, and Roger Thomas
Headwaters
to Ocean
Shellfish
Restoration
1. Non-tidal
2. Intertidal
3. Subtidal
1 2
3
CTUIR Freshwater Mussel Project
Nature’s Benefits
Bivalve Shellfish are “Ecosystem Engineers”
Kreeger
Oyster Reefs
Mussel Beds
Start
8 adult mussels No mussels
Biofiltration Potential
Slide from Dick Neves, VA Tech
Later
8 adult mussels No mussels
Slide from Dick Neves, VA Tech
Biofiltration Potential
•
1919 Since
1996
Kreeger
2012
Scientific Name Scientific Name DE NJ PA
ALASMIDONTA HETERODON DWARF WEDGEMUSSEL Endangered Endangered Critically Imperiled
ALASMIDONTA UNDULATA TRIANGLE FLOATER Extirpated ? Threatened Vulnerable
ALASMIDONTA VARICOSA BROOK FLOATER Endangered Endangered Imperiled
ANODONTA IMPLICATA ALEWIFE FLOATER Extremely Rare no data Extirpated ?
ELLIPTIO COMPLANATA EASTERN ELLIPTIO common common Secure
LAMPSILIS CARIOSA YELLOW LAMPMUSSEL Endangered Threatened Vulnerable
LAMPSILIS RADIATA EASTERN LAMPMUSSEL Endangered Threatened Imperiled
LASMIGONA SUBVIRIDIS GREEN FLOATER no data Endangered Imperiled
LEPTODEA OCHRACEA TIDEWATER MUCKET Endangered Threatened Extirpated ?
LIGUMIA NASUTA EASTERN PONDMUSSEL Endangered Threatened Critically Imperiled
MARGARITIFERA MARGARITIFERA EASTERN PEARLSHELL no data no data Imperiled
PYGANODON CATARACTA EASTERN FLOATER no data no data Vulnerable
STROPHITUS UNDULATUS SQUAWFOOT Extremely Rare Species of Concern Apparently Secure
State Conservation Status
Patchy, Impaired Extirpated Rare
Delaware River Basin
Freshwater Mussel Discoveries Tidal Delaware River:
Lots of animals 7 Species
Genetically Appropriate
Promise for Restoration
Questions:
How many mussels exist here?
How much water do they filter?
What happens to filtered material?
Do current populations benefit water quality?
Can mussel restoration improve water quality?
To Understand EcoServices, Need…
Physiology
Population Surveys
Ecology
Monitoring, Variability
Kreeger
Surveys
Determine current
mussel population
status
Identify sources for
restoration
Areas with Mussels:
Prioritize for
Conservation
Areas without Mussels:
Prioritize for
Restoration
Qualitative vs. Quantitative Surveys
Qualitative: • Opportunistic methods • Timed searches • Data on presence/absence, catch per unit effort • Assess large areas • Most common, cost effective Quantitative: • Intensive methods • Transects and quadrats • Data on densities, sizes, richness • Smaller areas • Rare, more costly Only way to assess ecosystem benefits
2012 Quantitative Surveys
Goals:
1. Quantify mussel species richness and density
2. Examine relationships with: • Depth (see Mills poster)
• Substrate (see Butler talk)
3. Estimate Potential Water Filtration per Bed
Tidal Delaware River
Shallow Subtidal Shorelines
Native Mussel Assemblages
Sample substrate
Methods
Four Sites
Shallow subtidal zone (0-8 feet below mean low water)
Transects: 8 per site
Quadrats: 3-4 per transect,
stratified by depth
Quadrat = 1m2 steel frame
Set up transects
Collect mussels
Haul to shore
Quadrat searches
Measure and ID
RTK GPS
Maps
Site 1
• Four mussel species
• Richness = 1.4 species m-2
• Density:
range = 0 – 29 mussels m-2
mean = 5.5 mussels m-2
See Mills and Butler presentations for depth and substrate
relationships, respectively
Pyganodon
cataracta Elliptio
complanata
Site 2
• Six mussel species
• Richness = 3.4 species m-2
• Density:
range = 0 – 80 mussels m-2
mean = 30.1 mussels m-2
See Mills and Butler presentations for depth and substrate
relationships, respectively
Pyganodon
cataracta Elliptio
complanata
Site 2
See Mills poster
Site 3
• Five mussel species
• Richness = 2.4 species m-2
• Density:
range = 0 – 129 mussels m-2
mean = 17.6 mussels m-2
See Mills and Butler presentations for depth and substrate
relationships, respectively
Elliptio
complanata
Site 4
• Five mussel species
• Richness = 2.4 species m-2
• Density:
range = 0 – 64 mussels m-2
mean = 10.8 mussels m-2
See Mills and Butler presentations for depth and substrate
relationships, respectively
Elliptio
complanata
How much do they weigh? No animals sacrificed in 2012
Dry tissue weights estimated from from earlier studies
11 species of freshwater mussels
653 animals (harvested 2000-2011)
LOG(ShellLength) = 4.22566 + 0.322226*LOG(DTW)
-4.6 -2.6 -0.6 1.4 3.4
LOG(DTW)
2.7
3.1
3.5
3.9
4.3
4.7
5.1
LO
G(S
hell
Len
gth
)
R2 = 80.0%
Species-specific weight estimates
sci_nameActinonaias ligamentinaAnodonta californianusAnodonta oregonensisElliptio complanataElliptio dilitataGonidea angulataLampsilis cariosaLeptodea ochraceaLigumia nasutaMargaratifera falcataPyganodon cataracta
Plot of Fitted Model
-4.6 -2.6 -0.6 1.4 3.4
LOG(DTW)
2.7
3.1
3.5
3.9
4.3
4.7
5.1L
OG
(Sh
ellL
en
gth
)sci_name
Actinonaias ligamentinaAnodonta californianusAnodonta oregonensisElliptio complanataElliptio dilitataGonidea angulataLampsilis cariosaLeptodea ochraceaLigumia nasutaMargaratifera falcataPyganodon cataracta
Plot of Fitted Model
-4.6 -2.6 -0.6 1.4 3.4
LOG(DTW)
2.7
3.1
3.5
3.9
4.3
4.7
5.1
LO
G(S
hellL
en
gth
)
R2 = 85.9%
Valu
e p
er
m2 (
mean %
±S
E)
Density (#)
Dry Tissue Weight (g)
0
10
20
30
40
50
60
70
80
90
Site 1
Site 2
Site 3
Site 4
C n=12 n=30BCB
A
a
bbb
Mussel Density and Total Weight by Site
Gra
ms / M
ussel
(mean ±
SE
)
Dry Tissue Weight / Density
0.0
0.5
1.0
1.5
2.0
2.5
3.0
3.5
Site 1
Site 2
Site 3
Site 4
A
B
B
A
Mussel Size by Site
Other Findings Species richness was positively related to density
Rarest species was Ligumia nasuta, eastern pondmussel – healthy size range from juveniles to old adults
Tidewater muckets were abundant
Juvenile mussels were abundant at 2 of 4 sites, suggesting reproduction is occuring
Plot of Fitted Model
Richness = 0.948775 + 0.816763*LOG(Density)
0 1 2 3 4 5
LOG(Density)
0
1
2
3
4
5
6
Ric
hn
ess
R2 = 67.3%
Total Mussel Population Size
Densities Extrapolated to Survey Areas
Quads (n)
Mussels per Quad (# m-2) Survey Area (m2)
Mussel Number
Average Std. Error (pooled)
Site 1 21 5.5 4.4 4,230 23,163
Site 2 27 30.1 3.9 9,504 286,175
Site 3 24 17.6 4.1 13,983 245,863
Site 4 24 10.8 4.1 10,658 115,458
4 Bed Totals> 96 16.8 38,375 670,660
2012 Abundance Surveys
Estimated Population Biomass per Site
Quads (n)
Mussels per Quad (# m-2)
Dry Tissue Weight per Quad (g m-2)
Survey Area (m2)
Mussel Number
Mussel Tissue Dry Weight
Average Std. Error (pooled) Average
Std. Error (pooled)
(g)
Site 1 21 5.5 4.4 17.5 8.8 4,230 23,163 74,210
Site 2 27 30.1 3.9 76.0 7.8 9,504 286,175 722,145
Site 3 24 17.6 4.1 16.5 8.3 13,983 245,863 230,725
Site 4 24 10.8 4.1 9.8 8.3 10,658 115,458 104,226
4 Bed Totals> 96 16.8 31.8 38,375 670,660 1,131,307
How much do they filter?
Apply Existing Clearance Rate Data
Lab Studies Field Studies
Kreeger
Review in Progress for Chesapeake Executive Order Study
Number of Species Diet
Clearance Rate
(L h-1 g-1)
Kryger and Riisgard (1988) 4 lab algae 1.11
Pusch et al. (2001) 2 field seston 0.38
Gatenby (2000) 3 lab algae 1.72
Silverman et al. (1995, 1997) 5 lab bacteria 0.77
Patterson (1984) 1 lab algae 0.38
Vanderploeg et al. (1995) 1 lab algae 1.45
Gatenby & Kreeger (2003) 6 field seston, lab algae 0.23
Kreeger (2011) 3 field seston 0.96
Mean > 0.875
Estimated Water Filtration
Quads (n)
Mussels per Quad (# m-2)
Dry Tissue Weight per Quad (g m-2)
Survey Area (m2)
Mussel Number
Mussel Tissue Dry
Weight
Typical Clearance
Rate
Typical Clearance
Rate
Bed Clearance Rate
Typical TSS Filtration
Average Std. Error (pooled) Average
Std. Error (pooled)
(g) (L hr-1 g DTW-1)
(gal day-1 g DTW-1)
(gal day-1) (metric tons
DW day-1)
Site 1 21 5.5 4.4 17.5 8.8 4,230 23,163 74,210
0.875 5.55
411,867 0.54
Site 2 27 30.1 3.9 76.0 7.8 9,504 286,175 722,145 4,007,906 5.29
Site 3 24 17.6 4.1 16.5 8.3 13,983 245,863 230,725 1,280,524 1.69
Site 4 24 10.8 4.1 9.8 8.3 10,658 115,458 104,226 578,456 0.76
4 Bed Totals> 96 16.8 31.8 38,375 670,660 1,131,307 6,278,754 8.29
Observations
Potential filtration of 6.3 million gallons per day for these 4 beds is: 2.5% of freshwater inflow from the Delaware River; and 1.6% of drinking water withdrawals for Philadelphia
Estimated suspended solids removal of 8.3 metric tons per day is: 121 times that by mussels in 6-mile reach of Brandywine River
More beds exist, especially in New Jersey
Study is limited to shallow subtidal shorelines, mussel densities increased with depth to limit of sampling
Water processing potential may not reflect actual water filtration
Many expected suitable sites had few or no mussels, especially where bed stability appeared compromised; habitat restoration would benefit mussel populations and ranges
Summary • Freshwater mussels are the most imperiled animals nationally
and locally
• Current freshwater mussel populations in the tidal Delaware
River are abundant enough to measurably help sustain water
quality
• For these reasons, critical habitat for mussels needs to be
mapped and protected
• Populations are far below historic levels basin-wide, and
mussel restoration would promote water quality and other
benefits
• More research is needed on physiological ecology of mussels
identify fates of filtered material and improve ecosystem service
models
Thanks to Our Funder: Pennsylvania Coastal Zone Management Program
www.DelawareEstuary.org
Extra Slides
DRBC
Desired Watershed Condition: A diverse and robust assemblage of native bivalves living in abundance in all available tidal and non-tidal ecological niches and providing maximum possible natural benefits.
Kreeger
>60 Species of Bivalves in the Delaware Estuary Watershed
DRBC
Crassostrea virginica
Elliptio complanata
Geukensia demissa
11 Other Species of Freshwater Unionid Mussels
Mya arenaria
Rangia cuneata
Corbicula fluminea
Mytilus edulis
Ensis directus
Mercenaria mercenaria
Freshwater Mussel Recovery Program 1. Surveys
• Establish current range and density for historically present species • Identify candidate areas to be conserved and/or restored • Qualitative (rapid) and Quantitative (intensive) • Delineate critical habitat to be protected
2. Restoration Suitability Tests • Assess if candidate restoration sites can sustain healthy mussel assemblages
3. Reintroduction • Transplant gravid broodstock from healthy extant populations nearby • Monitor success
4. Propagation • Produce genetically appropriate seed mussels in hatcheries for restocking
5. Education • Build awareness for mussel conservation and holistic restoration
6. Promote Habitat and Water Quality Improvement (e.g. dam removal)
Freshwater Mussel Recovery Program
0
200400
600800
1,0001,200
1,4001,600
1,8002,000
Millions of
Liters
Processed
1 2 4 6 8 10 15 30
Years After Planting
Series1
Not including progeny
Goals Based on Ecosystem Services